CN111666669A - Method for determining water replenishing rate of circulating water cooling system through concentration ratio - Google Patents
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- CN111666669A CN111666669A CN202010474577.1A CN202010474577A CN111666669A CN 111666669 A CN111666669 A CN 111666669A CN 202010474577 A CN202010474577 A CN 202010474577A CN 111666669 A CN111666669 A CN 111666669A
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 106
- 238000001816 cooling Methods 0.000 title claims abstract description 34
- 238000000034 method Methods 0.000 title claims abstract description 8
- -1 fluoride ions Chemical class 0.000 claims description 12
- 150000002500 ions Chemical class 0.000 claims description 12
- 229910001414 potassium ion Inorganic materials 0.000 claims description 8
- JLVVSXFLKOJNIY-UHFFFAOYSA-N Magnesium ion Chemical compound [Mg+2] JLVVSXFLKOJNIY-UHFFFAOYSA-N 0.000 claims description 6
- 229910001425 magnesium ion Inorganic materials 0.000 claims description 6
- 229910052710 silicon Inorganic materials 0.000 claims description 6
- 239000010703 silicon Substances 0.000 claims description 6
- 150000003839 salts Chemical class 0.000 claims description 5
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 claims description 4
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 claims description 4
- 229910001424 calcium ion Inorganic materials 0.000 claims description 4
- 238000001704 evaporation Methods 0.000 claims description 4
- 230000008020 evaporation Effects 0.000 claims description 4
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 4
- 229910052742 iron Inorganic materials 0.000 claims description 3
- 238000004519 manufacturing process Methods 0.000 claims description 3
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 claims description 2
- 229910052782 aluminium Inorganic materials 0.000 claims description 2
- 238000005286 illumination Methods 0.000 claims description 2
- 229910001415 sodium ion Inorganic materials 0.000 claims description 2
- 239000000126 substance Substances 0.000 claims 3
- 229910002651 NO3 Inorganic materials 0.000 claims 1
- 239000003795 chemical substances by application Substances 0.000 claims 1
- 239000013589 supplement Substances 0.000 claims 1
- 230000001502 supplementing effect Effects 0.000 claims 1
- 230000000694 effects Effects 0.000 abstract description 4
- NPYPAHLBTDXSSS-UHFFFAOYSA-N Potassium ion Chemical compound [K+] NPYPAHLBTDXSSS-UHFFFAOYSA-N 0.000 description 6
- 230000007774 longterm Effects 0.000 description 3
- 230000007613 environmental effect Effects 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- KRHYYFGTRYWZRS-UHFFFAOYSA-M Fluoride anion Chemical compound [F-] KRHYYFGTRYWZRS-UHFFFAOYSA-M 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 1
- FKNQFGJONOIPTF-UHFFFAOYSA-N Sodium cation Chemical compound [Na+] FKNQFGJONOIPTF-UHFFFAOYSA-N 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 239000013505 freshwater Substances 0.000 description 1
- 239000011777 magnesium Substances 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 238000013178 mathematical model Methods 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
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- G—PHYSICS
- G06—COMPUTING; CALCULATING OR COUNTING
- G06F—ELECTRIC DIGITAL DATA PROCESSING
- G06F30/00—Computer-aided design [CAD]
- G06F30/20—Design optimisation, verification or simulation
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- Engineering & Computer Science (AREA)
- Physics & Mathematics (AREA)
- Theoretical Computer Science (AREA)
- Computer Hardware Design (AREA)
- Evolutionary Computation (AREA)
- Geometry (AREA)
- General Engineering & Computer Science (AREA)
- General Physics & Mathematics (AREA)
- Treatment Of Water By Ion Exchange (AREA)
- Preventing Corrosion Or Incrustation Of Metals (AREA)
Abstract
本发明公开一种通过浓缩倍率确定循环水冷却系统补水率的方法,能够客观真实的反映出循环水系统的运行参数,及时调整和排查运行中存在问题,从而精确的控制系统的补水率,减少系统的新水消耗量,实现节能减排的效果。The invention discloses a method for determining the water replenishment rate of a circulating water cooling system through a concentration ratio, which can objectively and truly reflect the operating parameters of the circulating water system, adjust and check the problems existing in the operation in time, so as to accurately control the water replenishment rate of the system and reduce the The new water consumption of the system can achieve the effect of energy saving and emission reduction.
Description
技术领域technical field
本发明属于环境工程领域,特别涉及一种通过浓缩倍率确定循环水冷却系统补水率的方法。The invention belongs to the field of environmental engineering, and particularly relates to a method for determining the water replenishment rate of a circulating water cooling system through a concentration ratio.
背景技术Background technique
以钢铁企业为例,循环水冷却系统用途十分广泛,对于企业的生产必不可少。大部分的运行方式都是与设备进行换热后的水被提升泵输送到塔内,然后使水和空气之间进行热交换,或热、质交换,以达到降低水温的目的。Taking iron and steel enterprises as an example, the circulating water cooling system has a wide range of uses and is essential for the production of enterprises. Most of the operation modes are that the water after heat exchange with the equipment is transported into the tower by the lift pump, and then the heat exchange, or heat and mass exchange between the water and the air is carried out to achieve the purpose of lowering the water temperature.
国外发达国家的水系统的水务管理水平较高,一般都尽量考虑水的循环使用及处理后再使用,并考虑使用非传统水资源作为补充水源,以减少新水的用量和外排废水量。虽然目前国内的环保政策日趋严格,企业对水资源的管理也日趋重视,但尚未有用数学模型理论定量描述循环系统的浓缩倍率与补水率之间的相互关系。The water management level of the water system in foreign developed countries is relatively high. Generally, the recycling and reuse of water are considered as much as possible, and the use of non-traditional water resources as supplementary water sources is considered to reduce the amount of new water and the amount of wastewater discharged. Although the current domestic environmental protection policies are becoming more and more strict, and enterprises are paying more and more attention to the management of water resources, the relationship between the concentration rate and the water replenishment rate of the circulatory system has not been quantitatively described by mathematical model theory.
发明内容SUMMARY OF THE INVENTION
针对现有技术存在的不足,本发明提供一种通过浓缩倍率确定循环水冷却系统补水率的方法,能够客观真实的反映出循环水系统的运行参数,及时调整和排查运行中存在问题,从而精确的控制系统的补水率,减少系统的新水消耗量,实现节能减排的效果。In view of the deficiencies in the prior art, the present invention provides a method for determining the water replenishment rate of a circulating water cooling system through a concentration ratio, which can objectively and truly reflect the operating parameters of the circulating water system, adjust and check the problems in operation in time, so as to accurately Control the water replenishment rate of the system, reduce the new water consumption of the system, and achieve the effect of energy saving and emission reduction.
为了达到上述目的,本发明采用以下技术方案实现:In order to achieve the above object, the present invention adopts the following technical solutions to realize:
一种通过浓缩倍率确定循环水冷却系统补水率的方法,其特征在于:所述的循环水冷却系统为敞开式循环水冷却系统,包括所有管道阀门、冷却塔系统和生产工艺换热系统,并且处于稳定运行的状态;A method for determining the water replenishment rate of a circulating water cooling system by a concentration ratio, characterized in that: the circulating water cooling system is an open circulating water cooling system, including all pipeline valves, a cooling tower system and a production process heat exchange system, and in a stable state;
唯一进入循环水冷却系统的补水率为F0,循环水冷却系统排出水率包括F1和F2,其中F1是携带盐类物质排出的排出水率,F2是仅以水分子形式排出的排出水率;The only water replenishment rate entering the circulating water cooling system is F 0 , and the discharge water rate of the circulating water cooling system includes F 1 and F 2 , where F 1 is the discharge water rate that carries salts and F 2 is only discharged in the form of water molecules water discharge rate;
循环水冷却系统中各离子浓度为C11,C12,C13····C1(n-1),C1n,并且C11<C12<C13····C1(n-1)<C1n,相对应的补水中各离子浓度为C01,C02,C03····C0(n-1),C0n,循环水冷却系统的浓缩倍率N=(C11+C12+C13+····+C1(n-1)+C1n)/(C01+C02+C03+····+C0(n-1)+C0n),n取3-5;The concentration of each ion in the circulating water cooling system is C 11 , C 12 , C 13 · · · · · · · · · · · · · · C 1 (n-1) , C 1n , and C 11 <C 12 <C 13 · · · · · · · · C 1 (n- 1) <C 1n , the corresponding ion concentrations in the supplementary water are C 01 , C 02 , C 03 ··· C 0(n-1) , C 0n , the concentration ratio of the circulating water cooling system N=(C 11 +C 12 +C 13 +・・・+C 1(n-1) +C 1n )/(C 01 +C 02 +C 03 +・・・+C 0(n-1) +C 0n ) , n takes 3-5;
所述循环水冷却系统中的离子包括但不仅限于钠离子、钾离子、氯离子、氟离子、钙离子、镁离子、硫酸根离子、硝酸根离子、硅离子、铁离子和铝离子,在常温常压光照的条件下24h内的浓度不发生变化,并且周围环境的带入和系统投加的药剂中不含有该离子;The ions in the circulating water cooling system include but are not limited to sodium ion, potassium ion, chloride ion, fluoride ion, calcium ion, magnesium ion, sulfate ion, nitrate ion, silicon ion, iron ion and aluminum ion. The concentration does not change within 24h under the condition of normal pressure illumination, and the ion is not contained in the introduction of the surrounding environment and the system dosing;
所述的F0仅为人工补水,忽略自然条件的影响,包括但不仅限于下雨、下雪和冰雹;Described F 0 is only artificial water replenishment, ignoring the influence of natural conditions, including but not limited to rain, snow and hail;
所述的F1中含有与循环水冷却系统相同浓度的盐类物质,仅限于循环水冷却系统的排污,循环水冷却系统的漏损率为零,忽略但不限于飘散、飞溅、跑冒滴漏现象的影响;The F 1 contains the same concentration of salts as the circulating water cooling system, which is limited to the blowdown of the circulating water cooling system. The leakage rate of the circulating water cooling system is zero, ignoring but not limited to drifting, splashing, running and dripping. the effect of the phenomenon;
所述的F2以水分子的形态排到环境中,包括但不仅限于水表面的蒸发、物体表面的水分蒸发,在自然条件下为一个常数;The F 2 is discharged into the environment in the form of water molecules, including but not limited to the evaporation of water surface and the evaporation of water on the surface of objects, which is a constant under natural conditions;
依据水量平衡:F0=F1+F2;According to the water balance: F 0 =F 1 +F 2 ;
依据水质盐类物质平衡:F0=F1·NAccording to the water quality salt balance: F 0 =F 1 ·N
因此,F0=N·F2/(N-1)。Therefore, F 0 =N·F 2 /(N-1).
所述F2取值为0.01-0.02。The value of F 2 is 0.01-0.02.
本发明的有益效果在于:能够客观真实的得到循环系统的浓缩倍率数值,从而精确的控制系统的补水率,减少系统的新水消耗量,实现节能减排的效果。The beneficial effect of the invention is that the concentration ratio value of the circulation system can be obtained objectively and truly, so as to accurately control the water replenishment rate of the system, reduce the fresh water consumption of the system, and realize the effect of energy saving and emission reduction.
具体实施方式Detailed ways
下面结合具体实施例进行说明:Described below in conjunction with specific embodiments:
实施例1:Example 1:
一个长期稳定运行的敞开式循环水冷却系统,通过实际测量的补水率为0.02,F2的常数为0.01,循环系统中的钾离子浓度为11.2mg/L,镁离子为23.8mg/L,氯离子为42.1mg/L;补水中的钾离子浓度为3.8mg/L,镁离子为8.2mg/L,氯离子为14.1mg/L。A long-term stable operation of an open circulating water cooling system, the actual measured water replenishment rate is 0.02, the constant of F 2 is 0.01, the potassium ion concentration in the circulating system is 11.2mg/L, the magnesium ion is 23.8mg/L, and the chlorine ion is 23.8mg/L. The ion is 42.1mg/L; the potassium ion concentration in the replenishment water is 3.8mg/L, the magnesium ion is 8.2mg/L, and the chloride ion is 14.1mg/L.
因此N=(11.2+23.8+42.1)/(3.8+8.2+14.1)=2.95,So N=(11.2+23.8+42.1)/(3.8+8.2+14.1)=2.95,
系统补水率F0=2.95×0.01/(2.95-1)=0.015。The system water replenishment rate F 0 =2.95×0.01/(2.95-1)=0.015.
由于通过模型计算得到的系统真实补水率要小于实际测量得到的补水率,因此判定系统存在补水率偏高的问题。通过排查系统运行中存在的问题,从而降低实际补水率,实现新水用量的降低。Since the real water replenishment rate of the system calculated by the model is smaller than the actual measured water replenishment rate, it is determined that the system has a high water replenishment rate. By checking the problems existing in the operation of the system, the actual water replenishment rate can be reduced, and the consumption of new water can be reduced.
实施例2:Example 2:
一个长期稳定运行的敞开式循环水冷却系统,通过实际测量的补水率为0.026,F2的常数为0.015,循环系统中的硅离子浓度为1.3mg/L,钾离子为17.9mg/L,镁离子为21.5mg/L;补水中的硅离子浓度为0.24mg/L,钾离子为3.2mg/L,镁离子为5.1mg/L。A long-term stable operation of an open circulating water cooling system, the actual measured water replenishment rate is 0.026, the constant of F 2 is 0.015, the silicon ion concentration in the circulating system is 1.3mg/L, potassium ion is 17.9mg/L, magnesium ion is 17.9mg/L, magnesium The ion is 21.5mg/L; the silicon ion concentration in the replenishment water is 0.24mg/L, the potassium ion is 3.2mg/L, and the magnesium ion is 5.1mg/L.
因此N=(1.3+17.9+21.5)/(0.24+3.2+5.1)=4.77,So N=(1.3+17.9+21.5)/(0.24+3.2+5.1)=4.77,
系统补水率F0=4.77×0.015/(4.77-1)=0.019。The system water replenishment rate F 0 =4.77×0.015/(4.77-1)=0.019.
由于通过模型计算得到的系统真实补水率要小于实际测量得到的补水率,因此判定系统存在补水率偏高的问题。通过排查系统运行中存在的问题,从而降低实际补水率,实现新水用量的降低。Since the real water replenishment rate of the system calculated by the model is smaller than the actual measured water replenishment rate, it is determined that the system has a high water replenishment rate. By checking the problems existing in the operation of the system, the actual water replenishment rate can be reduced, and the consumption of new water can be reduced.
实施例3:Example 3:
一个长期稳定运行的敞开式循环水冷却系统,通过实际测量的补水率为0.032,F2的常数为0.02,循环系统中的硅离子浓度为2.4mg/L,钾离子为15.1mg/L,钙离子为48.6mg/L;补水中的硅离子浓度为1.54mg/L,钾离子为3.4mg/L,钙离子为13.6mg/L。A long-term stable operation of an open circulating water cooling system, the actual measured water replenishment rate is 0.032, the constant of F 2 is 0.02, the concentration of silicon ions in the circulating system is 2.4mg/L, potassium ions are 15.1mg/L, calcium ions are 15.1mg/L, calcium The ion is 48.6mg/L; the silicon ion concentration in the replenishment water is 1.54mg/L, the potassium ion is 3.4mg/L, and the calcium ion is 13.6mg/L.
因此N=(2.4+15.1+48.6)/(1.54+3.4+13.6)=3.57,So N=(2.4+15.1+48.6)/(1.54+3.4+13.6)=3.57,
系统补水率F0=3.57×0.02/(3.57-1)=0.028。The system water replenishment rate F 0 =3.57×0.02/(3.57-1)=0.028.
由于通过模型计算得到的系统真实补水率要小于实际测量得到的补水率,因此判定系统存在补水率偏高的问题。通过排查系统运行中存在的问题,从而降低实际补水率,实现新水用量的降低。Since the real water replenishment rate of the system calculated by the model is smaller than the actual measured water replenishment rate, it is determined that the system has a high water replenishment rate. By checking the problems existing in the operation of the system, the actual water replenishment rate can be reduced, and the consumption of new water can be reduced.
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Application publication date: 20200915 |